JP3429111B2 - Solid-liquid separation device - Google Patents

Solid-liquid separation device

Info

Publication number
JP3429111B2
JP3429111B2 JP23074795A JP23074795A JP3429111B2 JP 3429111 B2 JP3429111 B2 JP 3429111B2 JP 23074795 A JP23074795 A JP 23074795A JP 23074795 A JP23074795 A JP 23074795A JP 3429111 B2 JP3429111 B2 JP 3429111B2
Authority
JP
Japan
Prior art keywords
raw water
solid
water
filtration
filter
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP23074795A
Other languages
Japanese (ja)
Other versions
JPH0952003A (en
Inventor
輝雄 千田
憲次 中路
保 伊達
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toray Industries Inc
Original Assignee
Toray Industries Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toray Industries Inc filed Critical Toray Industries Inc
Priority to JP23074795A priority Critical patent/JP3429111B2/en
Publication of JPH0952003A publication Critical patent/JPH0952003A/en
Application granted granted Critical
Publication of JP3429111B2 publication Critical patent/JP3429111B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Filtration Of Liquid (AREA)

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、湖沼や池、濠、プ
ール、工業用水など大量の水を経済的に効率良く濾過す
る場合に有効な低水頭型固液分離装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a low-head type solid-liquid separation device effective for economically and efficiently filtering a large amount of water such as lakes, ponds, moats, pools and industrial water.

【0002】[0002]

【従来の技術】湖沼、池、プール、工業用水等の浄化用
の濾過装置として、充填層式の砂濾過装置、長毛濾布を
用いた回転ドラム式濾過装置は既に知られている。
2. Description of the Related Art As a filter for purifying lakes, ponds, pools, industrial water, etc., a packed bed type sand filter and a rotary drum type filter using a long hair filter cloth are already known.

【0003】しかしながら、このような従来の濾過装置
は、前者の砂濾過装置においては濾層厚みが通常100
0mm程度で、一方後者の長毛濾布を用いた回転ドラム
式濾過装置においては濾層厚みが20〜40mmであ
り、両装置とも濾層の内部で固形成分を捕捉し固液分離
操作を行うものである。
However, in such a conventional sand filter, the thickness of the filter layer is usually 100 in the former sand filter.
0 mm, on the other hand, in the latter rotary drum type filter using a long-hair filter cloth, the filter layer has a thickness of 20 to 40 mm, both of which perform solid-liquid separation operation by capturing solid components inside the filter layer. Is.

【0004】これらの従来方法では、濾過に要する濾過
圧は、通常、損失水頭として1m〜5m程度の高水頭が
必要となり、原水を濾過装置部分に供給するのに、通常
ポンプを用いる。
In these conventional methods, the filtration pressure required for filtration usually requires a high head of about 1 m to 5 m as a head loss, and a pump is usually used to supply raw water to the filter unit.

【0005】ところが、このようにポンプを用いる供給
方式では、本発明で対象としている、湖沼、池、プー
ル、工業用水等大量の水を処理する場合、高圧力にする
ことでポンプの電力費が高くつく、また、ポンプの高圧
化に伴い、原水中に含まれる固形成分にかかる機械的剪
断力が増大し、ポンプ内部および移送配管中で被濾過液
(原水)中の固形成分が微細化し、固液分離装置による
固形成分除去率が低下するといった問題があった。
However, in such a supply system using a pump, when a large amount of water such as lakes, ponds, pools, and industrial water, which is the object of the present invention, is to be treated, the power cost of the pump is increased by increasing the pressure. It is expensive, and as the pressure of the pump increases, the mechanical shearing force applied to the solid components contained in the raw water increases, and the solid components in the liquid to be filtered (raw water) become finer inside the pump and in the transfer pipe, There is a problem that the solid component removal rate by the solid-liquid separation device is reduced.

【0006】特に湖沼や池等で発生する生物系の動植物
性プランクトン、工業用水浄化工程で発生する凝集フロ
ック等は、このような機械的剪断力に弱く、固液分離性
能が低下するため大きな問題となる。
[0006] In particular, biological flora and fauna of biological systems generated in lakes and ponds, floc flocs generated in industrial water purification process, etc. are vulnerable to such mechanical shearing force and the solid-liquid separation performance is deteriorated, which is a serious problem. Becomes

【0007】[0007]

【発明が解決しようとする課題】本発明の課題は、これ
らの問題を解消するために、原水を濾過装置に供給する
ポンプを用いることなく、濾過圧力を低く保ち、かつ、
固形成分の除去率ならびに濾過速度を高く保つことが可
能で、湖沼や池、プール、工業用水等の大量の原水を効
率よく経済的に浄化することが可能な固液分離装置を提
供することにある。
SUMMARY OF THE INVENTION In order to solve these problems, an object of the present invention is to maintain a low filtration pressure without using a pump for supplying raw water to a filtration device, and
To provide a solid-liquid separation device capable of maintaining a high solid component removal rate and a high filtration rate, and capable of efficiently and economically purifying a large amount of raw water such as lakes, ponds, pools, and industrial water. is there.

【0008】[0008]

【課題を解決するための手段】上記課題を解決するため
に、本発明の固液分離装置は、原水貯留池からの原水
を、胴に濾材を装着してなる濾過ドラムの内側に導入
し、前記濾過ドラムを回転させながら前記濾材を通過さ
せることによって前記原水中の固液を分離するようにし
た固液分離装置において、少なくとも前記原水貯留池か
ら前記濾過ドラムの内側までの原水の流路を、水頭差に
基づいて原水が自然流下する流路に構成し、かつ、前記
原水貯留池と前記濾過ドラムとの間に、原水に凝集剤を
投入する凝集反応槽を設けたことを特徴とするものから
なる。上記原水貯留池と上記濾過ドラムとの間で原水に
凝集剤を投入することにより、固液成分を凝集させて濾
過効率を向上させることができる。この凝集剤は、アニ
オン系の高分子凝集剤を含んでいることが好ましい。
In order to solve the above-mentioned problems, the solid-liquid separation device of the present invention introduces raw water from a raw water reservoir into the inside of a filtration drum having a filter medium mounted on a cylinder, so as to separate the solid-liquid of the raw water by passing the filter medium while rotating the filtration drum
In the solid-liquid separation device, at least the flow path of raw water from the raw water reservoir to the inside of the filtration drum has a head difference.
Based on the flow path that the raw water naturally flows based on,
A coagulant is added to the raw water between the raw water reservoir and the filtration drum.
It is characterized in that a coagulation reaction tank for charging is provided . Raw water between the raw water reservoir and the filtration drum
By adding a flocculant, the solid-liquid components are flocculated and filtered.
The over-efficiency can be improved. This coagulant is
It is preferable to include an on-type polymer flocculant.

【0009】[0009]

【0010】[0010]

【0011】[0011]

【0012】[0012]

【0013】本装置においては、上記濾過ドラムから処
理水受池に至る処理水の流路を、さらに、水頭差に基づ
いて処理水が自然流下する流路に構成することができ
る。また、原水貯留池から処理水受池に至る流路を複数
段直列に配することもできる。
In the present apparatus, the flow path of the treated water from the filtration drum to the treated water reservoir can be further configured as a flow path in which the treated water naturally flows down based on the head difference. Further, the flow path from the raw water storage pond to the treated water reception pond can be arranged in multiple stages in series.

【0014】さらに濾過ドラムからの処理水を原水貯
留池に戻すポンプを設けるようにしてもよい。濾過後の
処理水であるから、ポンプを用いても、固形成分の微細
化等の問題は生じない。
Further , a pump for returning the treated water from the filtration drum to the raw water reservoir may be provided. After filtration
Since it is treated water, even if a pump is used
There is no problem such as commutation.

【0015】[0015]

【発明の実施の形態】以下に、本発明の固液分離装置
望ましい実施の形態について、図面を参照して説明す
る。図1は、本発明をたとえばゴルフ場の池の浄化に適
用した実施態様を示している。図2は、図1の浄化工程
中に用いられている回転式濾過ドラム装置の回転軸に対
し直角方向に切断した断面を示している。
BEST MODE FOR CARRYING OUT THE INVENTION Preferred embodiments of the solid-liquid separation device of the present invention will be described below with reference to the drawings. FIG. 1 shows an embodiment in which the present invention is applied to cleaning a pond of a golf course, for example. FIG. 2 shows a cross section of the rotary filtration drum device used in the purification step of FIG. 1 taken in a direction perpendicular to the rotation axis.

【0016】本実施態様は、ゴルフ場の上池1の液面1
1と下池4の液面41との水頭差ΔH2 を利用して、原
水貯留池としての上池1の水(原水)を本発明の固液分
装置により濾過ドラム装置に自然流下式に導き、固形
成分を除いて、浄化後の水(処理水)を処理水受池とし
ての下池4に供給するようにしたものである。
In this embodiment, the liquid surface 1 of the upper pond 1 of the golf course is
1 and the water level difference ΔH 2 between the liquid surface 41 of the lower pond 4 are used to guide the water (raw water) of the upper pond 1 as a raw water storage pond to the filtration drum device by the solid-liquid separation device according to the present invention. The purified water (treated water), excluding solid components, is supplied to the lower pond 4 as a treated water receiving pond.

【0017】本実施態様における構成を説明するに、上
池1からの原水は、上池流出管12を通して、前処理装
置としての凝集反応槽2に送られる。この凝集反応槽2
の入口近傍には、凝集剤21の供給ライン22が設けら
れ、槽2内には、流入側にもぐり堰板23、流出側にじ
ゃま板24が設けられ、両板23、24の間に攪拌機2
5が設けられている。上記もぐり堰板23、流出側のじ
ゃま板24は、凝集反応槽2内で凝集剤と原水とが良好
に混合し凝集反応でフロックが生成され易いように、ま
た、凝集剤がショートパスして添加した薬剤がむだにな
らないように付加してある。
To explain the configuration of this embodiment, raw water from the upper pond 1 is sent to the coagulation reaction tank 2 as a pretreatment device through the upper pond outflow pipe 12. This aggregation reaction tank 2
A supply line 22 for the coagulant 21 is provided in the vicinity of the inlet of the tank, a burr weir plate 23 is provided on the inflow side, and a baffle plate 24 is provided on the outflow side in the tank 2, and a stirrer is provided between the two plates 23, 24. Two
5 are provided. The muffle weir plate 23 and the outflow-side baffle plate 24 facilitate mixing of the flocculant and the raw water in the flocculation reaction tank 2 to easily generate flocs in the flocculation reaction, and the flocculation agent is short-passed. The added drug is added so that it is not wasted.

【0018】凝集反応槽2の流出口26は、槽の低部に
設けられ、回転式の濾過ドラム装置3の流入口と連通さ
れている。ただし、この接続管は必ずしも凝集反応槽2
の低部に設ける必要はなく、次の回転式濾過ドラム装置
3の原水供給部における液面37よりも下部の位置であ
ればよい。これは、凝集反応槽2の液面と濾過ドラム装
置3の原水供給部の液面37がほぼ同一となるように連
通させることにより、原水が配管中を移動する際に、凝
集フロック化した固形成分にポンプ等による機械的な剪
断力がかからず、フロックが微細化しないため、次工程
の固液分離を効率良く行うことができるようにするため
である。
The outflow port 26 of the flocculation reaction tank 2 is provided at a lower portion of the tank and communicates with the inflow port of the rotary filtration drum device 3. However, this connecting pipe is not always the agglutination reaction tank 2
Need not be provided at a lower part of the above, and may be located at a position lower than the liquid level 37 in the raw water supply part of the next rotary filtration drum device 3. This is because the liquid level of the flocculation reaction tank 2 and the liquid level 37 of the raw water supply section of the filtration drum device 3 are communicated so that they are substantially the same, and when the raw water moves in the pipe, the flocculated solids are formed. This is because the components are not subjected to mechanical shearing force by a pump or the like and the flocs are not miniaturized, so that solid-liquid separation in the next step can be efficiently performed.

【0019】すなわち、上池1からの原水は、上池流出
管12、凝集反応槽2、その流出口26を介して濾過ド
ラム装置3の回転濾過ドラム31の内側へと導入される
が、本浄化工程においては、少なくともここまでの原水
の導入が、水頭差ΔH3 に基づく自然流下によって行わ
れる。ここまでの送液にポンプを使用しないので、原水
に機械的な剪断力が加わらず、該剪断力によって固形成
分が微細化されたり、凝集剤投入によりフロックされた
固形成分が微細化されたりしない。この状態で、原水が
濾過ドラム装置3に導入される。
That is, the raw water from the upper pond 1 is introduced into the inside of the rotary filtration drum 31 of the filtration drum device 3 through the upper pond outflow pipe 12, the flocculation reaction tank 2, and its outlet 26. In the purification step, at least the raw water so far is introduced by natural flow based on the head difference ΔH 3 . Since no pump is used for feeding the liquid up to this point, no mechanical shearing force is applied to the raw water, and the shearing force does not atomize the solid component or the floced solid component due to the addition of the coagulant. . In this state, raw water is introduced into the filtration drum device 3.

【0020】回転式の濾過ドラム装置3は、たとえば特
公平4−9081号公報に記載されているような装置に
構成される。図1、図2を参照して説明するに、濾過ド
ラム装置3には、胴の内面に濾材(濾布)32を装着し
てなる濾過ドラム31が設けられており、ドラム31
は、モータ33によって回転駆動されるようになってい
る。回転駆動される濾過ドラム31と非回転の固定部と
の間には、洩れ防止のためのシールゴム34が設けられ
ている。この濾過ドラム31の内側に凝集反応槽2から
の原水が導入され、濾過ドラム31を回転させながら原
水が濾材32を通過することにより、原水中の固液が分
離されるようになっている。導入された原水は、濾過ド
ラム31内の濾過装置流入側液面37と、これよりも低
い、濾過装置流出側液面38との濾過損失水頭差ΔH1
によって濾材32を通過し、浄水(処理水)となって、
濾過ドラム装置3からの流出管39を通って下池4に供
給される。
The rotary filtration drum device 3 is constructed as a device described in, for example, Japanese Patent Publication No. 4-9081. As will be described with reference to FIGS. 1 and 2, the filtration drum device 3 is provided with a filtration drum 31 having a filter material (filter cloth) 32 attached to the inner surface of the body.
Are rotated by a motor 33. A seal rubber 34 for preventing leakage is provided between the rotatably driven filtration drum 31 and the non-rotating fixed portion. Raw water from the coagulation reaction tank 2 is introduced into the inside of the filtration drum 31, and the raw water passes through the filter medium 32 while rotating the filtration drum 31, whereby the solid-liquid in the raw water is separated. The introduced raw water has a filtration loss head difference ΔH 1 between the filtering device inflow side liquid level 37 in the filtering drum 31 and the filtering device outflow side liquid level 38 lower than this.
Passes through the filter medium 32 and becomes purified water (treated water),
It is supplied to the lower pond 4 through the outflow pipe 39 from the filtration drum device 3.

【0021】原水中の固形成分は、濾材32で捕捉さ
れ、捕捉された固形成分は濾過ドラム31の回転に従い
水面上に移動し、その最上部近傍で濾過ドラム31の外
側より、洗浄ポンプ35によって汲み上げた濾過水を、
濾布逆洗ライン35aに接続された逆洗スプレーノズル
35bから噴射される逆洗水で逆洗される。逆洗水は、
固形成分を含む排水として、洗浄水排出ライン36を経
て系外に排出される。しかし、原水や濾材の種類によっ
ては、濾材に捕捉された固形成分を逆洗だけでは十分に
除去することが困難な場合がある。この場合には、濾過
ドラム31の内側に濾布表洗ライン35cに接続された
表洗スプレーノズル35dを設け、該スプレーノズル3
5dから濾材表面に向けて噴射される表洗水で表面側に
残留している固形水分を濾過ドラム31内に洗い落し、
再度濾材を通して濾過するようにすると、濾材の目詰り
の進行を防ぐことができ効果的である。
The solid component in the raw water is captured by the filter medium 32, and the captured solid component moves to the water surface as the filter drum 31 rotates. The filtered water pumped up,
It is backwashed with the backwash water sprayed from the backwash spray nozzle 35b connected to the filter cloth backwash line 35a. Backwash water
Waste water containing solid components is discharged to the outside of the system through the cleaning water discharge line 36. However, depending on the type of raw water or the filter medium, it may be difficult to sufficiently remove the solid components captured by the filter medium only by backwashing. In this case, the surface washing spray nozzle 35d connected to the filter cloth surface washing line 35c is provided inside the filter drum 31, and the spray nozzle 3
The solid water remaining on the surface side is washed off into the filter drum 31 with surface washing water sprayed from 5d toward the surface of the filter medium,
Filtering through the filter material again is effective in preventing the clogging of the filter material from progressing.

【0022】なお、濾過された処理水中の固形成分濃度
をできる限り低く保つためには、上記表洗スプレーノズ
ル35dの向きを変え、表洗スプレー水にて洗い落され
た固形成分を逆洗排水と同様にドラム中央部の洗浄排水
受水部36aに受け、洗浄排水ライン36を経て系外に
排出することも可能である。
In order to keep the concentration of the solid component in the filtered treated water as low as possible, the direction of the surface washing spray nozzle 35d is changed and the solid component washed off with the surface washing spray water is backwashed and drained. In the same manner as above, it is also possible to receive it in the cleaning drainage water receiving portion 36a at the center of the drum and discharge it to the outside of the system via the cleaning drainage line 36.

【0023】上記回転式の濾過ドラム装置3に使用する
濾材32は、織物または編物からなる基材の表面に、そ
の基材を立毛してなる太さ0.1〜20μmの極細繊維
の立毛が一方向に横たわって濾過層を形成するものであ
る。横たわってとは、直立していない、あるいは寝かせ
てというほどの意味である。濾材32となる織物または
編物の表面の立毛は、通常、太さが0.1〜20μmの
ポリアミド、ポリエステル、ポリオレフィン、ポリビニ
ルアルコール系、ポリフルオロエチレン、ポリアクリロ
ニトリルなどの合成繊維の極細繊維で構成されたものを
使用する。織成や編成の種類はとくに問わないが、織物
では朱子織物が、編物ではハーフ編のトリコット生地は
立毛方法の一つの手段である起毛がしやすく好ましい。
太さが0.1μm未満の極細繊維では強度が不足し、2
0μmを越える繊維は起毛後、直立しやすく、良好な濾
過層を形成しにくい難点がある。立毛方法は、従来から
の公知の手段を用いればよい。
The filter medium 32 used in the rotary type filtration drum device 3 has naps of ultrafine fibers having a thickness of 0.1 to 20 μm formed by napping the base material made of woven or knitted material. It lies in one direction and forms a filtration layer. Lying means not standing upright or lying down. The naps on the surface of the woven or knitted material to be the filter medium 32 are usually made of ultrafine synthetic fibers such as polyamide, polyester, polyolefin, polyvinyl alcohol, polyfluoroethylene and polyacrylonitrile having a thickness of 0.1 to 20 μm. Use what you have. The type of weaving or knitting is not particularly limited, but a satin woven fabric is preferable for the woven fabric, and a half knitted tricot fabric is preferable for the knitted fabric because it is easily raised as one means of the napping method.
Ultrafine fibers with a thickness of less than 0.1 μm lack strength and
Fibers having a diameter of more than 0 μm tend to stand upright after being raised, which makes it difficult to form a good filtration layer. For the napped method, a conventionally known means may be used.

【0024】このような濾材を使用するのは、この濾材
が単に池や湖沼に多く発生するアオコ等の植物性プラン
クトンの分離に好適であるという理由だけではない。本
発明者らの研究の結果、まず第1に、上述のように極細
繊維の立毛が一方向に横たわって濾過層を形成するとい
うことは、言い換えればその部分で従来の砂濾過濾層と
同等に微細粒子を分離できる緻密層を形成することとな
り、上記濾材が単に上記植物性プランクトンの除去だけ
でなく、従来から課題となっていた寒天状の生物系のス
ライムや、凝集剤で凝集された凝集フロック等を効率良
く分離できること、第2に、同濾材が、その厚みが1.
5mm以下と薄いことから、通常、湖沼等で発生する植
物性プランクトン主体で懸濁物質濃度が20mg/l程
度の原水を対象とする場合、濾過圧は最大でも水頭圧6
00mm程度に抑えることができ、しかもそのときの濾
過速度(処理水量)が900(m3 /m2 ・日)と高い
値が得られるという特徴を有していることによる。
The use of such a filter medium is not the only reason that the filter medium is simply suitable for separating phytoplankton such as blue-green algae which often occur in ponds and lakes. As a result of the research conducted by the present inventors, firstly, the fact that the naps of the ultrafine fibers lie in one direction to form the filtration layer as described above means that, in other words, that portion is equivalent to the conventional sand filtration layer. In order to form a dense layer capable of separating fine particles, the filter medium not only removes the phytoplankton, but also agar-like biological slime, which has been a problem in the past, and was aggregated with an aggregating agent. The floc and the like can be efficiently separated. Secondly, the filter medium has a thickness of 1.
Since it is as thin as 5 mm or less, when the target is phytoplankton, which is usually generated in lakes and marshes, and the concentration of suspended matter is about 20 mg / l, the filtration pressure is 6 at the maximum.
This is because it has a feature that it can be suppressed to about 100 mm, and that the filtration rate (amount of treated water) at that time is as high as 900 (m 3 / m 2 · day).

【0025】このような特徴を備えた濾材を適用するこ
とにより原水内の微細な固形成分を低損失水頭で、かつ
高速で効率良く捕捉できると同時に、捕捉された固形成
分は濾材が薄いことにより、水スプレーによる逆洗なら
びに表洗により濾材表面側に剥離し易いこと、即ち濾材
の洗浄再生が容易であることにつながり、連続的に使っ
ても、長期間にわたって目詰りせず、濾過水量が低下し
ない事実を見出したことが本発明につながった一つの要
因である。
By applying a filter medium having such characteristics, it is possible to efficiently capture fine solid components in raw water with a low loss head and at a high speed, and at the same time, the solid components captured are thin because the filter medium is thin. , Back-washing with water spray and surface washing facilitate peeling on the surface of the filter medium, that is, easy cleaning and regeneration of the filter medium, even if used continuously, it will not clog for a long period of time, and the amount of filtered water will be large. Finding the fact that it does not decrease is one of the factors that led to the present invention.

【0026】[0026]

【0027】上記のような濾過ドラム装置3で濾過され
た処理水は、流出管39を通して処理水受池としての下
池4に送られる。本実施態様においては、この送水もま
た、ポンプ等を用いることなく、水頭差に基づく自然流
下によって行われる。つまり、濾過ドラム装置3の流出
側の液面38と下池4の液面41との水頭差に基づき自
然流下される。
The treated water filtered by the filtering drum device 3 as described above is sent to the lower pond 4 as a treated water receiving reservoir through the outflow pipe 39. In the present embodiment, this water supply is also carried out by natural flow based on the head difference without using a pump or the like. In other words, the liquid surface 38 on the outflow side of the filtration drum device 3 and the liquid surface 41 of the lower pond 4 are naturally flown down based on the head difference.

【0028】次に、図3に本発明の別の実施態様に係る
固液分離装置を示す。本実施態様においては、原水貯留
池から処理水受池に至る工程が複数段(本実施態様では
2段)直列に配されている。1段目の工程の原水貯留池
51からの原水が固液分離され、処理水が処理水受池5
2に送られる。この1段目の処理水受池52が2段目の
工程の原水貯留池となり、該貯留池からの原水が固液分
離され、処理水が処理水受池53に送られる。
Next, FIG. 3 shows a solid-liquid separator according to another embodiment of the present invention. In this embodiment, the steps from the raw water storage pond to the treated water storage pond are arranged in multiple stages (two stages in this embodiment) in series. The raw water from the raw water storage pond 51 in the first step is solid-liquid separated, and the treated water is treated water receiving pond 5
Sent to 2. The treated water receiving basin 52 of the first stage serves as a raw water storage basin of the second stage, the raw water from the reservoir is subjected to solid-liquid separation, and the treated water is sent to the treated water receiving basin 53.

【0029】原水貯留池51からの原水は、流出ライン
54、開閉弁55を介して第1段目の濾過ドラム装置5
6に水頭差に基づいて自然流下され、濾過された処理水
が受槽57内に一時的に貯留される。受槽57からオー
バフローした処理水が、処理水受池52(第2段目原水
貯留池)へと自然流下される。処理水受池52からの原
水が、同様に、流出ライン58を通過して濾過ドラム装
置59へと自然流下され、濾過された処理水が受槽60
に一時的に貯留された後、受槽60からオーバフローし
た処理水が処理水受池53へと自然流下される。受槽5
7又は受槽60のいずれか一方または両方に、ポンプ6
1又はポンプ62を設け、処理水の一部を原水貯留池5
1に戻すようにしてもよい。
Raw water from the raw water storage pond 51 is passed through the outflow line 54 and the opening / closing valve 55 to the first-stage filtration drum device 5
The treated water that has been naturally flowed down to the water tank 6 based on the head difference is filtered and temporarily stored in the receiving tank 57. The treated water that overflows from the receiving tank 57 naturally flows down to the treated water receiving reservoir 52 (second-stage raw water storage reservoir). Similarly, the raw water from the treated water receiving reservoir 52 naturally flows down to the filtration drum device 59 through the outflow line 58, and the filtered treated water is received in the receiving tank 60.
After being temporarily stored in the treated water, the treated water overflowing from the receiving tank 60 naturally flows down to the treated water receiving reservoir 53. Receiving tank 5
7 or the receiving tank 60, or both, pump 6
1 or a pump 62 is provided, and a part of the treated water is stored in the raw water reservoir 5
You may make it return to 1.

【0030】このように、各池の立地条件を活かして、
処理工程を複数段配することもできる。
In this way, taking advantage of the location conditions of each pond,
It is also possible to arrange a plurality of processing steps.

【0031】図4に、本発明のさらに別の実施態様に係
る固液分離装置を示す。本実施態様においては、原水貯
留池71の原水が、流入管72を通して浮上設置された
濾過ドラム装置73に水頭差に基づいて自然流下によっ
て導入され、濾過された処理水は受槽74に一時的に貯
留された後、ポンプ75によって原水貯留池71に戻さ
れるようになっている。
FIG. 4 shows a solid-liquid separator according to still another embodiment of the present invention. In the present embodiment, the raw water of the raw water storage pond 71 is introduced into the filtration drum device 73 floated through the inflow pipe 72 by gravity flow based on the head difference, and the filtered treated water is temporarily stored in the receiving tank 74. After the water is stored, it is returned to the raw water storage pond 71 by the pump 75.

【0032】また、図5には図4に示した装置の変形例
を示すが、本実施態様においては装置が湖中(池中)に
設置されている。すなわち、原水貯留池81の原水が、
流入管82を通して湖中設置された濾過ドラム装置83
に水頭差に基づいて自然流下により導入される。水頭差
をもたせることができるよう、濾過ドラム装置83から
原水貯留池81の液面上方まで、大気解放管84が延び
ている。濾過された処理水は受槽85に一時的に貯留さ
れた後、ポンプ86によって原水貯留池81に戻される
ようになっている。
FIG. 5 shows a modification of the apparatus shown in FIG. 4, but in the present embodiment, the apparatus is installed in a lake (in a pond). That is, the raw water of the raw water reservoir 81
Filter drum device 83 installed in the lake through the inflow pipe 82
It is introduced by gravity flow based on the head difference. An atmosphere release pipe 84 extends from the filtration drum device 83 to a position above the liquid surface of the raw water reservoir 81 so as to have a head difference. The filtered treated water is temporarily stored in the receiving tank 85 and then returned to the raw water reservoir 81 by the pump 86.

【0033】このように、濾過ドラム装置73、83に
より濾過された処理水を再び原水貯留池71、81に戻
すようにしてもよい。少なくとも濾過ドラム装置73、
83に導入されるまでの原水に、ポンプ等による機械的
剪断力がかからないようにしておくことにより、濾過ド
ラム装置73、83での濾過処理まで、固形成分が微細
化されることを防止できる。
The treated water thus filtered by the filtering drum devices 73 and 83 may be returned to the raw water storage basins 71 and 81 again. At least a filter drum device 73,
It is possible to prevent the solid component from becoming fine until the filtration treatment by the filtration drum devices 73 and 83 by preventing the raw water from being introduced into 83 before being subjected to mechanical shearing force by a pump or the like.

【0034】[0034]

【実施例】富栄養化した公園池で発生したアオコ(ミク
ロキィスティス);懸濁物質濃度(SS)=20mg/
l〔アオコ細胞数=2500個/ml〕を原水とし、本
発明で好適に用いられる前述の如き濾材を使用した濾過
ドラムを設け、原水を水頭差に基づく自然流下によって
導入、処理した場合と、従来法の急速砂濾過装置を用い
た場合とを比較し、本発明による効果を確認した。
[Examples] Blue-green algae (microcystis) generated in a eutrophication park pond; suspended solid concentration (SS) = 20 mg /
1 [blue water cell number = 2500 cells / ml] is used as raw water, a filter drum using the above-mentioned filter material suitably used in the present invention is provided, and the raw water is introduced and treated by natural flow based on the head difference. The effect of the present invention was confirmed by comparison with the case of using a conventional rapid sand filter.

【0035】本発明の濾材として次の製法により製作し
た濾布を用いた。すなわち、ポリエステルを島成分と
し、ポリスチレンを海成分とする18芯の太さが20μ
mの複合繊維を紡糸した。この複合繊維を紡績して得ら
れた20/2Sの紡績糸を緯糸とし、太さが10μmの
ポリエステル繊維を48本束ねたものを経糸として、緯
糸が30本/cm、経糸が40本/cmの5枚朱子織物
を織成した。さらに、この織物からトリクロルエチレン
を溶媒として緯糸のポリスチレンを除去し、太さ約2.
4μmの極細繊維約2000本を緯糸とする織物に加工
した。加工された織物を起毛機を用いて、経糸方向に2
0回、反対方向に10回の起毛操作を行って、主に緯糸
を起毛し、2.4μmの立毛を有し立毛数が約1000
本/mmの立毛朱子織物を製造した。
A filter cloth manufactured by the following method was used as the filter medium of the present invention. In other words, the thickness of 18 cores with polyester as the island component and polystyrene as the sea component is 20μ.
m composite fiber was spun. A spun yarn of 20 / 2S obtained by spinning this composite fiber was used as a weft, and a bundle of 48 polyester fibers having a thickness of 10 μm was used as a warp. The weft was 30 / cm and the warp was 40 / cm. 5 sheets of satin fabric were woven. Furthermore, the polystyrene of the weft yarn was removed from this woven fabric by using trichlorethylene as a solvent, and the thickness was about 2.
About 2000 pieces of 4 μm ultrafine fibers were processed into a woven fabric. Using a raising machine, add 2 to the processed fabric in the warp direction.
Raising is performed 0 times and 10 times in the opposite direction to nap mainly the weft, and has 2.4 μm naps and a nap count of about 1000.
A book / mm napped satin fabric was produced.

【0036】本濾布の物性は目付が180g/m2 であ
り、平均目開きは7.5μmであった(7.5μmの粒
子が50%除去可能なことを示す)。一方砂濾過は、砂
粒子の平均径が0.64mm、均等係数ψ=1.50、
濾層厚み1000mmの充填濾層を用いた。
The physical properties of this filter cloth were a basis weight of 180 g / m 2 and an average opening of 7.5 μm (showing that particles of 7.5 μm can be removed by 50%). On the other hand, in sand filtration, the average diameter of sand particles is 0.64 mm, the uniform coefficient ψ = 1.50,
A packed filter layer having a filter layer thickness of 1000 mm was used.

【0037】テスト条件は、上記一定濃度の原水を濾過
圧(損失水頭)を100mmから1600mmまで変化
させて供給し、一定量の濾過水量が得られるまでの時間
と、収集した一定量の濾過水のSS濃度を分析し、それ
ぞれ原水濃度との比較により、SSの除去率ならびに各
濾過圧における濾過速度(処理水量)を算出し、それを
図6にまとめた。図中A、aが本発明による固液分離、
B、bが比較例濾材を示す。
The test conditions were as follows: the raw water of the above-mentioned constant concentration was supplied while changing the filtration pressure (head loss) from 100 mm to 1600 mm, the time until a certain amount of filtered water was obtained, and the collected constant amount of filtered water. The SS concentration was analyzed, and the removal rate of SS and the filtration rate (amount of treated water) at each filtration pressure were calculated by comparison with the raw water concentration, respectively, and are summarized in FIG. In the figure, A and a are solid-liquid separation according to the present invention,
B and b show comparative example filter media.

【0038】図6より、濾過圧が両濾材のSS除去率に
与える影響は同様の挙動特性を示すが、明らかに濾過圧
が損失水頭600mm以上となると、粒子が微細化し除
去率の低下現象がみられる。濾過速度に関しては、従来
の砂濾過に比べ、本発明の濾材では5〜6倍の濾過速度
が得られている。それも濾過圧が損失水頭600mm以
下、好ましくは400mm以下にて大きな差が現れてい
る。
As shown in FIG. 6, the influence of the filtration pressure on the SS removal rate of both filter media shows the same behavior characteristics. However, when the filtration pressure exceeds 600 mm of head loss, the particles become finer and the removal rate lowers. Seen. Regarding the filtration rate, the filtration rate of the filter material of the present invention is 5 to 6 times that of the conventional sand filtration. There is also a large difference in the filtration pressure when the head loss is 600 mm or less, preferably 400 mm or less.

【0039】図6に示す比較より、本発明による固液分
離においては、原水移送用のポンプを用いることなく、
600mm以下の低損失水頭領域においても高濾過速度
が得られる。特に、池や湖沼、プール、工業用水等大水
量の濾過が必要な分野では、水を移送するのにポンプを
用いると、そのための消費電力は非常に大きくなるが、
本発明の固液分離装置を用いることにより、極めて大き
な経済的効果が得られる。つまり、安価に大量の原水の
処理が可能となる。
From the comparison shown in FIG. 6, in the solid-liquid separation according to the present invention, a pump for transferring raw water was used,
A high filtration rate can be obtained even in a low-loss head area of 600 mm or less. Especially in fields such as ponds, lakes, pools, and industrial water where a large amount of water needs to be filtered, using a pump to transfer water results in extremely high power consumption.
By using the solid-liquid separation device of the present invention, an extremely large economic effect can be obtained. That is, a large amount of raw water can be treated at low cost.

【0040】また、本発明装置では、濾過圧として水頭
600mm以下でも運転できることにより、本実施例の
如く、固液分離装置の原水側液面(図1の上池の液面1
1)と処理水側液面(下池の液面41)との差が600
mm程度あれば、液の移送用ポンプは完全に不要とな
り、自然流下にて円滑に固液分離処理ができることにな
る。
Further, the present invention apparatus, by which can be operated as a filtration pressure even hydrocephalus 600mm or less, as in the present embodiment, the raw water side liquid surface of the solid-liquid separator (upper reservoir of the liquid level 1 in FIG. 1
The difference between 1) and the liquid level on the treated water side (liquid level 41 of the lower pond) is 600.
If the thickness is about mm, the liquid transfer pump is completely unnecessary, and the solid-liquid separation process can be smoothly performed under natural flow.

【0041】更に図6より、上記実施例では、損失水頭
600mm以上になると、送液のドライブがかかりす
ぎ、固形成分に与える機械的剪断力が大となるため、固
形成分に微細化が生じてSSの除去率も低下する。この
ように本発明の如く低損失水頭による固液分離が、SS
の除去率、および、液移送のための消費電力費の両面か
ら効率の良い方法であり、装置であることがわかる。
Further, from FIG. 6, in the above-mentioned embodiment, when the head loss was 600 mm or more, the drive of the liquid feed was excessively applied, and the mechanical shearing force applied to the solid component became large, so that the solid component was miniaturized. The removal rate of SS also decreases. Thus, the solid-liquid separation by the low-loss head as in the present invention is
It can be seen that the method is an efficient method and is an apparatus from the viewpoints of both the removal rate and the power consumption cost for liquid transfer.

【0042】このように、本発明の装置は、前述の池や
湖沼等の他、特に大水量の処理が必要となる河川、ダム
工事現場ならびに建設現場での工事余水の処理、海の埋
立て時に発生する余水の処理などに用いると経済的な効
果が大で好適である。
Thus, in addition to the above-mentioned ponds, lakes and marshes, the apparatus of the present invention treats especially rivers, dam construction sites and construction spillage at construction sites, and sea reclamation that require treatment of large amounts of water. It is suitable because it has a large economic effect when it is used for treatment of residual water that sometimes occurs.

【0043】また、海底浚渫ヘドロ等にて海を埋立てる
時に上澄として発生する余水の処理には、従来2種以上
の凝集剤を添加して、凝集フロックを形成後処理するの
が一般的であったが、本発明の方法ならびに装置を用い
ることにより、アニオン系の高分子凝集剤を原水SSの
2/10,000〜5/10,000程度と非常に少量
添加することにより、効率良く固液分離できることも判
明しており、この分野への適用は大きな経済的な効果と
ともに、凝集剤過剰添加による地球環境の汚染を防止で
きるといった効果も期待できる。
Further, in the treatment of residual water generated as a supernatant when the sea is filled with seabed dredging sludge or the like, it is common to add two or more kinds of flocculants to treat flocculated flocs after formation. However, by using the method and apparatus of the present invention, it is possible to improve the efficiency by adding an anionic polymer flocculant in a very small amount of about 2 / 10,000 to 5 / 10,000 of raw water SS. It is also known that solid-liquid separation can be performed well, and application to this field is expected to have a large economic effect as well as the effect of preventing pollution of the global environment due to excessive addition of a coagulant.

【0044】上記アニオン系の高分子凝集剤としては、
たとえば、ポリアクリルアミド系のサンフロックAH−
150P(三洋化成工業株式会社製)、ハイモロックS
S−120(株式会社ハイモ社製)などが使用できる。
As the anionic polymer flocculant,
For example, polyacrylamide-based Sunfloc AH-
150P (manufactured by Sanyo Chemical Industry Co., Ltd.), Hymoloc S
S-120 (made by Hymo Co., Ltd.) etc. can be used.

【0045】[0045]

【発明の効果】以上詳述したように、本発明の固液分離
装置によるときは、原水に凝集剤を投入する凝集反応槽
を設けるとともに、少なくとも原水貯留池から濾過ドラ
ムまでの原水の導入を、水頭差に基づく自然流下によっ
て行うようにしたので、少なくともこの間でポンプ等に
よる機械的な剪断力が作用することを防止でき、原水中
の固形成分の微細化を抑制して、大量の原水を低コスト
でありながら効率良く固液分離処理できる。
As described above in detail, the solid-liquid separation of the present invention
When using a device, a flocculation reaction tank that adds a flocculant to raw water
With the provision of, at least the raw water from the raw water reservoir to the filtration drum is introduced by natural flow based on the head difference, so that mechanical shearing force by a pump or the like can be prevented from acting at least during this period. By suppressing the miniaturization of the solid components in the raw water, a large amount of raw water can be efficiently solid-liquid separated at low cost.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の一実施態様に係る固液分離装置の概略
構成図である。
FIG. 1 is a schematic configuration diagram of a solid-liquid separation device according to an embodiment of the present invention.

【図2】図1のII−II線に沿う濾過ドラム装置の拡
大縦断面図である。
FIG. 2 is an enlarged vertical cross-sectional view of the filtration drum device taken along line II-II in FIG.

【図3】本発明の別の実施態様に係る固液分離装置の概
略構成図である。
FIG. 3 is a schematic configuration diagram of a solid-liquid separation device according to another embodiment of the present invention.

【図4】本発明のさらに別の実施態様に係る固液分離装
置の概略構成図である。
FIG. 4 is a schematic configuration diagram of a solid-liquid separator according to still another embodiment of the present invention.

【図5】図4の装置の変形例に係る固液分離装置の概略
構成図である。
5 is a schematic configuration diagram of a solid-liquid separation device according to a modified example of the device of FIG.

【図6】実施例および比較例におけるSS除去率および
濾過速度(処理水量)と濾過圧(損失水頭)との関係図
である。
FIG. 6 is a diagram showing the relationship between the SS removal rate, filtration rate (amount of treated water), and filtration pressure (head loss) in Examples and Comparative Examples.

【符号の説明】[Explanation of symbols]

1 原水貯留池としての上池 2 凝集反応槽 3 回転式濾過ドラム装置 4 処理水受池としての下池 11 上池液面 12 上池流出管 21 凝集剤 22 凝集剤供給ライン 23 もぐり堰板 24 じゃま板 25 攪拌機 31 濾過ドラム 32 濾材(濾布) 33 モータ 34 シールゴム 35 洗浄ポンプ 35a 濾布逆洗ライン 35b 逆洗スプレーノズル 35c 濾布表洗ライン 35d 表洗スプレーノズル 36 洗浄水排出ライン 36a 洗浄排水受水部 37 濾過装置流入側液面 38 濾過装置流出側液面 39 濾過装置流出管 41 下池液面 51、71、81 原水貯留池 52 処理水受池(第2段目の原水貯留池) 53 処理水受池 56、59、73、83 回転式濾過ドラム装置 ΔH1 濾過損失水頭 ΔH2 上池液面と下池液面の水頭差 ΔH3 原水貯留池から濾過ドラム導入側までの水頭差1 Upper Pond as Raw Water Reservoir 2 Coagulation Reaction Tank 3 Rotary Filtration Drum Device 4 Lower Pond as Treatment Water Reservoir 11 Upper Pond Liquid Level 12 Upper Pond Outflow Pipe 21 Flocculant 22 Flocculant Supply Line 23 Mug Weir Board 24 Jam Plate 25 Stirrer 31 Filtering drum 32 Filter material (filter cloth) 33 Motor 34 Seal rubber 35 Cleaning pump 35a Filter cloth backwash line 35b Backwash spray nozzle 35c Filter cloth surface wash line 35d Surface wash spray nozzle 36 Wash water discharge line 36a Wash drainage receiver Water part 37 Filtration device inflow side liquid level 38 Filtration device outflow side liquid level 39 Filtration device outflow pipe 41 Lower pond liquid levels 51, 71, 81 Raw water storage reservoir 52 Treated water receiving reservoir (second stage raw water reservoir) 53 Treatment filtration drum introduced from the water受池56,59,73,83 rotary drum filter device [Delta] H 1 filtered headloss [Delta] H 2 upper reservoir liquid level and the water head difference lower reservoir liquid level [Delta] H 3 raw water pond Water head difference of up to

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平6−238110(JP,A) 特開 昭55−111811(JP,A) 特開 平7−116418(JP,A) 特開 昭51−117450(JP,A) 実開 昭55−88818(JP,U) (58)調査した分野(Int.Cl.7,DB名) B01D 33/06 ZAB ─────────────────────────────────────────────────── --Continued from the front page (56) References JP-A-6-238110 (JP, A) JP-A-55-111811 (JP, A) JP-A-7-116418 (JP, A) JP-A51- 117450 (JP, A) Actual development Sho 55-88818 (JP, U) (58) Fields investigated (Int.Cl. 7 , DB name) B01D 33/06 ZAB

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 原水貯留池からの原水を、胴に濾材を装
着してなる濾過ドラムの内側に導入し、前記濾過ドラム
を回転させながら前記濾材を通過させることによって前
記原水中の固液を分離するようにした固液分離装置にお
いて、少なくとも前記原水貯留池から前記濾過ドラムの
内側までの原水の流路を、水頭差に基づいて原水が自然
流下する流路に構成し、かつ、前記原水貯留池と前記濾
過ドラムとの間に、原水に凝集剤を投入する凝集反応槽
を設けたことを特徴とする固液分離装置。
1. Raw water from a raw water storage pond is introduced into the inside of a filter drum having a filter medium mounted on a cylinder, and the solid liquid in the raw water is passed by passing the filter medium while rotating the filter drum. In a solid-liquid separator designed to separate
In addition, at least the raw water flow path from the raw water reservoir to the inside of the filtration drum is filled with natural water based on the head difference.
It is configured to flow down and the raw water reservoir and the filter are
Coagulation reaction tank that puts a coagulant into raw water between the drum and
A solid-liquid separation device comprising:
【請求項2】 前記濾過ドラムから処理水受池に至る処
理水の流路が、水頭差に基づいて処理水が自然流下する
流路に構成されている、請求項1の固液分離装置。
2. A process from the filtration drum to the treated water reservoir
The flow path of the treated water naturally flows down the treated water based on the head difference.
The solid-liquid separation device according to claim 1, wherein the solid-liquid separation device is configured in a flow path .
【請求項3】 前記原水貯留池から処理水受池に至る
が複数段直列に配されている、請求項2の固液分離
置。
3. The flow from the raw water storage pond to the treated water reception pond
The solid-liquid separation device according to claim 2, wherein the channels are arranged in a plurality of stages in series.
Place
【請求項4】 前記濾過ドラムからの処理水を前記原水
貯留池に戻すポンプが設けられている、請求項1の固液
分離装置。
4. The solid-liquid separation device according to claim 1 , further comprising a pump for returning the treated water from the filtration drum to the raw water reservoir .
JP23074795A 1995-08-15 1995-08-15 Solid-liquid separation device Expired - Fee Related JP3429111B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP23074795A JP3429111B2 (en) 1995-08-15 1995-08-15 Solid-liquid separation device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP23074795A JP3429111B2 (en) 1995-08-15 1995-08-15 Solid-liquid separation device

Publications (2)

Publication Number Publication Date
JPH0952003A JPH0952003A (en) 1997-02-25
JP3429111B2 true JP3429111B2 (en) 2003-07-22

Family

ID=16912662

Family Applications (1)

Application Number Title Priority Date Filing Date
JP23074795A Expired - Fee Related JP3429111B2 (en) 1995-08-15 1995-08-15 Solid-liquid separation device

Country Status (1)

Country Link
JP (1) JP3429111B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4605898B2 (en) * 2000-12-22 2011-01-05 株式会社技研製作所 Civil engineering water treatment method
JP2012148205A (en) * 2011-01-15 2012-08-09 Maeda Corp Rotary drum filter
JP6377239B1 (en) * 2017-12-26 2018-08-22 株式会社クボタ Coagulation and mixing apparatus, water purification system and floc forming method

Also Published As

Publication number Publication date
JPH0952003A (en) 1997-02-25

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